JP2005111441A - Microbiologically treatable molding and biological treatment apparatus - Google Patents

Microbiologically treatable molding and biological treatment apparatus Download PDF

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JP2005111441A
JP2005111441A JP2003352298A JP2003352298A JP2005111441A JP 2005111441 A JP2005111441 A JP 2005111441A JP 2003352298 A JP2003352298 A JP 2003352298A JP 2003352298 A JP2003352298 A JP 2003352298A JP 2005111441 A JP2005111441 A JP 2005111441A
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plate member
microbiologically
treatable
molding
flat plate
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Keiichi Asami
圭一 浅見
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Unitika Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a microbiologically treatable molding which has high strengths and exerts such a good influence on a microbiologically treatable molding-incorporated unit that the rising time since the operation of the unit is started until the unit comes into a stable condition can be made short and with which organic matter in the water to be treated is removed excellently, and to provide a biological treatment apparatus using the microbiologically treatable molding as a microbe carrying carrier. <P>SOLUTION: The microbiologically treatable molding is obtained by superimposing a flat plate-shaped member 2 on a corrugated plate-shaped member 1 containing an activated carbon fiber. The flat plate-shaped member 2 is composed of a textile fabric. The peak height (H) of the corrugated plate-shaped member 1 is 5-100 mm and the peak pitch (P) is 5-100 mm. The flat plate-shaped member 2 can be composed of a synthetic resin film. This microbiologically treatable molding is used in the biological treatment apparatus as the microbe carrying carrier. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、観賞魚、養殖用水の浄化、水耕栽培水の浄化、食品工場排水、厨房排水、下水など有機物を含む一般排水処理、半導体工場の排水処理、及び半導体産業等で用いられる超純水の使用後の回収システム等に、微生物担体として組込んで使用することができる微生物処理用成形体と生物処理装置に関するものである。   The present invention is an ultrapure used in ornamental fish, aquaculture water purification, hydroponics water purification, food factory effluent, kitchen effluent, general effluent treatment including organic matter such as sewage, semiconductor factory effluent treatment, semiconductor industry, etc. The present invention relates to a molded article for microorganism treatment and a biological treatment apparatus that can be used as a microorganism carrier in a recovery system after use of water.

現在、微生物担体として活性炭を用いて水処理する生物活性炭法の研究が盛んである。生物活性炭法は、微生物と基質の接触時間の増大や、阻害因子の吸着除去などの作用で、難分解性物質の処理が可能となり、また、生物処理効率の上昇などをもたらすと言われている。   At present, research on a biological activated carbon method in which water is treated using activated carbon as a microorganism carrier is actively conducted. The biological activated carbon method is said to be able to treat difficult-to-decompose substances by increasing the contact time between microorganisms and substrates, and adsorption and removal of inhibitory factors, and to increase biological treatment efficiency. .

従来、生物活性炭法に用いられる担体としては、球状又は粒状の活性炭が使用され、処理方式としては流動床法(up flow)や固定床法(down flow)があるが、流動床法(up flow)による処理が一般的である。しかし、流動床法には、次のような欠点がある。
(1)曝気洗浄を行なうと、活性炭が流出するため、生物処理槽の洗浄ができず、このため長時間の運転を行うと、槽内の微生物量が多くなり過ぎて処理能力が低下する。
(2)微粉炭が発生するため、後段に膜分離装置が設置されている場合には、後段の膜分離装置に目詰まりが発生する。
(3)活性炭が生物膜によって凝集して塊状になり、槽壁等に付着することにより、被処理液の流れが不均一になる(いわゆる片流れを生じる)。
(4)活性炭を流動状態に保つことが難しく、保守が繁雑である。
(5)流動状態を保つために槽内の被処理水量を大きくする必要があるので、槽以外に循環槽を設けて、ここで曝気をする形式の間接曝気になる。
(6)流動床の場合には、流動状態で活性炭が相互に衝突するため、固定床の場合に比べて表面に付着する生物膜がはがれやすい傾向にある。このため、特に、半導体産業における使用後の超純水のような、有機物濃度の低い被処理水を処理する場合のように、微生物の増殖速度が本来的に遅い場合には、装置が運転を開始してから安定状態になるまでの時間(立ち上がり時間)が長くなる。
Conventionally, spherical or granular activated carbon is used as a carrier used in the biological activated carbon method, and there are a fluidized bed method (up flow) and a fixed bed method (down flow) as a treatment method, but a fluidized bed method (up flow). ) Is common. However, the fluidized bed method has the following drawbacks.
(1) When aeration cleaning is performed, activated carbon flows out, so that the biological treatment tank cannot be cleaned. Therefore, if the operation is performed for a long time, the amount of microorganisms in the tank becomes excessive and the processing capacity decreases.
(2) Since pulverized coal is generated, clogging occurs in the downstream membrane separator when the downstream membrane separator is installed.
(3) The activated carbon is aggregated and formed into a lump by the biofilm and adheres to the tank wall or the like, whereby the flow of the liquid to be treated becomes non-uniform (so-called single flow occurs).
(4) It is difficult to keep activated carbon in a fluid state, and maintenance is complicated.
(5) Since it is necessary to increase the amount of water to be treated in the tank in order to maintain the fluid state, indirect aeration of a type in which a circulation tank is provided in addition to the tank and aeration is performed here.
(6) In the case of a fluidized bed, activated carbon collides with each other in a fluidized state, so that the biofilm attached to the surface tends to be peeled more easily than in the case of a fixed bed. For this reason, especially when the growth rate of microorganisms is inherently slow, such as when treating water to be treated with a low concentration of organic matter, such as ultrapure water after use in the semiconductor industry, the device operates. The time (rise time) from the start to the stable state becomes longer.

一方、球状、あるいは粒状の活性炭を用いた固定床法(down flow)による処理においては、活性炭の周囲の生物膜が比較的短時間で肥大化し、すぐに目詰まりを起こすという問題がある。   On the other hand, in the treatment by the fixed bed method (down flow) using spherical or granular activated carbon, there is a problem that the biofilm around the activated carbon is enlarged in a relatively short time and is immediately clogged.

上記の問題を解決するために、特許文献1には、フェルト布状活性炭繊維を波板状になるように不織布に貼着した成形体を使用する生物処理装置が提案されている。   In order to solve the above problems, Patent Document 1 proposes a biological treatment apparatus that uses a molded body in which felt cloth-like activated carbon fibers are attached to a nonwoven fabric so as to be corrugated.

しかしながら、この装置では、フェルト布状活性炭繊維を貼着する不織布がルーズな構造であるため、成形体の強度が弱いという問題があった。
特許第3107950号公報
However, this apparatus has a problem that the strength of the molded body is weak because the nonwoven fabric to which the felt cloth-like activated carbon fibers are attached has a loose structure.
Japanese Patent No. 3107950

本発明は、上記の問題を解決し、強度が高く、かつ、組み込んだ装置が運転を開始してから安定状態になるまでの立ち上がり時間が短く,被処理水中の有機物の除去に優れた微生物処理用成形体と、この微生物処理用成形体を微生物担体として用いた生物処理装置を提供することを技術的な課題とするものである。   The present invention solves the above problems, has a high strength, and has a short rise time from the start of operation of the built-in apparatus until it becomes stable, and is excellent in the removal of organic substances in the water to be treated. It is a technical problem to provide a molded article for use and a biological treatment apparatus using the molded article for microorganism treatment as a microorganism carrier.

本発明者は、上記の課題を解決するために鋭意検討した結果、活性炭繊維を主成分とする波板状部材の山の形態を適切に規定するとともに、波板状部材を接着させる平板状部材として、織編物や合成樹脂フイルムで構成された部材を用いればよいことを知見して本発明に到達した。   As a result of intensive studies to solve the above problems, the inventor of the present invention appropriately defines the shape of the corrugated plate-like member mainly composed of activated carbon fiber and adheres the corrugated plate-like member to the flat plate-like member. As a result, the inventors have found that a member composed of a woven or knitted fabric or a synthetic resin film may be used, and reached the present invention.

すなわち、本発明は、次の構成を要旨とするものである。
(1)平板状部材と、活性炭繊維を含有する波板状部材とが重ねられてなる成形体であって、前記平板状部材が織編物で構成され、かつ、波板状部材の山高さが5〜100mm、山のピッチが5〜100mmであることを特徴とする微生物処理用成形体。
(2)平板状部材と、活性炭繊維を含有する波板状部材とが重ねられてなる成形体であって、前記平板状部材が合成樹脂フイルムで構成され、かつ、波板状部材の山高さが5〜100mm、山のピッチが5〜100mmであることを特徴とする微生物処理用成形体。
(3)上記(1)又は(2)記載の微生物処理用成形体を微生物担体として用いた生物処理装置。
That is, the gist of the present invention is as follows.
(1) A molded body formed by laminating a flat plate member and a corrugated plate member containing activated carbon fibers, wherein the flat plate member is formed of a woven or knitted fabric, and the peak height of the corrugated plate member is A molded article for treating microorganisms, characterized in that it has a pitch of 5 to 100 mm and a mountain pitch of 5 to 100 mm.
(2) A molded body in which a flat plate-like member and a corrugated plate-like member containing activated carbon fibers are overlaid, wherein the flat plate-like member is composed of a synthetic resin film, and the peak height of the corrugated plate-like member 5 to 100 mm, and the pitch of the mountain is 5 to 100 mm.
(3) A biological treatment apparatus using the microorganism treatment molded article according to (1) or (2) as a microorganism carrier.

本発明によれば、強度が高くて長寿命であり、かつ、組み込んだ装置が運転を開始してから安定状態になるまでの立ち上がり時間が短く,被処理水中の有機物の除去に優れた微生物処理用成形体と、この微生物処理用成形体を微生物担体として用いた生物処理装置が提供される。   According to the present invention, the microorganism treatment is high in strength, has a long life, and has a short rise time from the start of operation of the built-in apparatus until it becomes stable, and is excellent in removing organic substances in the water to be treated. And a biological treatment apparatus using the microorganism treatment molded body as a microorganism carrier.

以下、本発明について詳細に説明する。   Hereinafter, the present invention will be described in detail.

本発明の微生物処理用成形体は、平板状部材と波板状部材とが重ねられてなる成形体である。例えば図1で示したように、波板状部材1と平板状部材2とが上下に接合されており、波板状部材1と平板状部材2との間に透孔3が存在して本発明の微生物処理用成形体Xが形成されている。   The molded article for microbial treatment of the present invention is a molded article in which a flat plate member and a corrugated plate member are stacked. For example, as shown in FIG. 1, the corrugated plate member 1 and the flat plate member 2 are joined up and down, and a through hole 3 exists between the corrugated plate member 1 and the flat plate member 2, so that The molded article X for microbial treatment of the invention is formed.

波板状部材は、活性炭繊維とバインダー繊維とを主成分としたシート状物を波板状に加工したものである。波板状部材となるシート状物としては、微生物の担持性や、活性炭繊維の脱落及び経済性を考慮すると、目付が40〜200g/m2、活性炭繊維含有量が5〜40質量%、厚みが0.2〜5mmであるものが好ましく、目付が50〜100g/m2、活性炭繊維含有量が10〜30質量%、厚みが0.5〜3mmのシートがより好ましい。 The corrugated plate member is obtained by processing a sheet-like material mainly composed of activated carbon fiber and binder fiber into a corrugated plate shape. As a sheet-like material to be a corrugated member, in consideration of the supportability of microorganisms, dropping of activated carbon fibers and economic efficiency, the basis weight is 40 to 200 g / m 2 , the activated carbon fiber content is 5 to 40% by mass, and the thickness. Is preferably 0.2 to 5 mm, more preferably a sheet having a basis weight of 50 to 100 g / m 2 , an activated carbon fiber content of 10 to 30% by mass, and a thickness of 0.5 to 3 mm.

波板状部材に用いられる活性炭繊維は、石炭ピッチ系、フェノール系、及びセルロース系繊維等から合成されたものが使用できる。活性炭繊維の比表面積は、500〜2500m2/gであることが好ましい。
活性炭繊維とともに波板状部材に用いられるバインダー繊維としては、ポリエステル、ポリアミド、エチレンビニルアルコール(EVA)、ポリプロピレンやポリエチレンなどのポリオレフィンからなる芯鞘構造の複合繊維である熱融着性繊維が好ましく、芯、鞘部ともポリオレフィンからなるバインダー繊維が、微生物で分解され難いので特に好ましい。
As the activated carbon fiber used for the corrugated plate member, those synthesized from coal pitch-based, phenol-based, cellulose-based fiber and the like can be used. The specific surface area of the activated carbon fiber is preferably 500 to 2500 m 2 / g.
The binder fiber used for the corrugated plate member together with the activated carbon fiber is preferably a heat-fusible fiber which is a composite fiber having a core-sheath structure made of polyolefin such as polyester, polyamide, ethylene vinyl alcohol (EVA), polypropylene or polyethylene, Binder fibers made of polyolefin for both the core and the sheath are particularly preferable because they are hardly decomposed by microorganisms.

波板状部材とともに本発明の微生物処理用成形体を形成する平板状部材としては、産業資材用に用いられる織編物や合成樹脂フイルムを採用することができるが、通水性、通気性の面からは織編物,特に剛性のあるメッシュ状のものが好ましい。織物や編物は,それらを構成する糸条が連続(フイラメント)するか又は撚で拘束されて(紡績糸)おり、その上, 織組織や編組織で拘束されているので,不織布より強度が高く、また、合成樹脂フイルムは、繊維より強力が大きいため、いずれも本発明の微生物処理用成形体の強度を向上させることができる。   As the flat plate member that forms the molded article for microbial treatment of the present invention together with the corrugated plate member, a woven or knitted fabric or a synthetic resin film used for industrial materials can be adopted, but from the viewpoint of water permeability and air permeability. Is preferably a woven or knitted fabric, particularly a rigid mesh. Woven fabrics and knitted fabrics have higher strength than non-woven fabrics because the yarns constituting them are continuous (filaments) or constrained by twisting (spun yarns), and also constrained by woven or knitted fabrics. In addition, since the synthetic resin film is stronger than the fiber, any of them can improve the strength of the molded article for microbial treatment of the present invention.

平板状部材を構成するポリマーとしては、織編物、合成樹脂フイルムとも、ポリエチレン、ポリプロピレンなどのポリオレフィン、ナイロン6,ナイロン6.6などのポリアミド、ポリエチレンテレフタレート、ポロブチレンテレフタレートなどのポリエステルを採用することができる。また、織編物にはガラス繊維からなるものも使用することができるが、ポリオレフィンからなる平板状部材は、微生物で分解され難いので好ましい。   As the polymer constituting the flat plate member, both woven and knitted fabrics and synthetic resin films may be polyolefins such as polyethylene and polypropylene, polyamides such as nylon 6 and nylon 6.6, polyesters such as polyethylene terephthalate and polybutylene terephthalate. it can. Moreover, although what consists of glass fiber can also be used for a woven / knitted fabric, since the flat plate member which consists of polyolefin is hard to be decomposed | disassembled by microorganisms, it is preferable.

本発明で使用される平板状部材は、織編物、合成樹脂フイルムともに、厚みが30〜500μm,特に50〜300μmのものが好ましい。また、メッシュ状の織編物の場合は、50mm間の糸本数が10〜100本、特に20〜50本のものが好ましい。   The flat members used in the present invention preferably have a thickness of 30 to 500 μm, particularly 50 to 300 μm for both woven and knitted fabrics and synthetic resin films. Moreover, in the case of a mesh-like woven or knitted fabric, the number of yarns between 50 mm is preferably 10 to 100, and more preferably 20 to 50.

本発明の微生物処理用成形体は、波板状部材の山高さ(H)5〜100mm、ピッチ(P)5〜100mmであることが必要であり、山高さ8〜80mm、ピッチ8〜80mmが好ましく、山高さ10〜50mm、ピッチ10〜50mmがより好ましい。波板状部材の山高さやピッチが5mm未満になると、波板状部材と平板状部材とを接合して形成される透孔に微生物が詰まりやすくなり、排水処理の能力が低下する。また、波板状部材の山高さやピッチが100mmを超えると、微生物と排水の接触がうまくいかず、良好な排水処理ができなくなる。   The molded body for microbial treatment of the present invention needs to have a peak height (H) of 5 to 100 mm and a pitch (P) of 5 to 100 mm of the corrugated member, and the peak height of 8 to 80 mm and the pitch of 8 to 80 mm. Preferably, the peak height is 10 to 50 mm and the pitch is 10 to 50 mm. If the peak height or pitch of the corrugated member is less than 5 mm, microorganisms are likely to be clogged in the through holes formed by joining the corrugated member and the flat member, and the ability of wastewater treatment is reduced. Moreover, when the peak height or pitch of the corrugated plate member exceeds 100 mm, the contact between the microorganisms and the waste water is not successful, and a good waste water treatment cannot be performed.

本発明の微生物処理用成形体は、例えば図2で示したような生物処理装置の処理槽4内に充填し(固定床)、被処理水タンク5からポンプ6で被処理水を下方から処理槽4内に供給するとともに、エアポンプ7で空気を処理槽4内に吹込んで処理し、処理槽4の上部から処理液を取り出すものである。   The molded article for microbial treatment of the present invention is filled in a treatment tank 4 of a biological treatment apparatus as shown in FIG. 2 (fixed bed), and treated water is treated from below by a treated water tank 5 with a pump 6. While supplying into the tank 4, it processes by blowing air in the process tank 4 with the air pump 7, and takes out a process liquid from the upper part of the process tank 4. FIG.

次に、本発明の微生物処理用成形体の製法例について説明する。   Next, an example of a method for producing the molded article for microbial treatment of the present invention will be described.

まず、活性炭繊維とバインダー繊維とを所定の質量比で混綿した後、ランダムカード、パラレルカード等のカード機を用い、活性炭繊維とバインダー繊維からなるフェルト状活性炭繊維シートを形成する。   First, after blending the activated carbon fiber and the binder fiber at a predetermined mass ratio, a felt-like activated carbon fiber sheet composed of the activated carbon fiber and the binder fiber is formed using a card machine such as a random card or a parallel card.

このようにして形成したフェルト状活性炭繊維シートをシングルフエザーやダブルフエザーで加工して波板状部材とし、これと平板状部材とを重ね合わせ、その接点をホットメルト接着剤で接着して図1のようなハニカム状の微生物処理用成形体を製造する。このようにして作製した微生物処理用成形体を、さらに多段に重ね合わせ接着することによりブロック状の微生物処理用成形体とすることもできる。また、図1の微生物処理用成形体を筒状に巻き上げることにより円筒状の微生物処理用成形体とすることもできる。   The felt-like activated carbon fiber sheet formed in this way is processed into a corrugated plate member by processing with a single feather or a double feather, and this and a flat plate member are overlapped, and the contact is bonded with a hot melt adhesive. A honeycomb-shaped molded article for microbial treatment is produced. The microorganism-treated molded body thus produced can be made into a block-shaped microorganism-treated molded body by further overlapping and adhering in multiple stages. Moreover, it can also be set as the cylindrical microbial treatment molded object by winding up the microbial treatment molded object of FIG. 1 in a cylinder shape.

波板状部材と平板状部材とを接着させるための接着剤としては、ポリエステル、ポリアミド、ポリオレフィン、エチレンビニルアルコール(EVA)などのホットメルト接着剤が好ましく使用できるが、ポリオレフィン、EVAなどのホットメルト接着剤が微生物分解され難いので特に好ましい。   As an adhesive for bonding the corrugated plate member and the flat plate member, a hot melt adhesive such as polyester, polyamide, polyolefin, ethylene vinyl alcohol (EVA) or the like can be preferably used, but a hot melt adhesive such as polyolefin or EVA can be used. The adhesive is particularly preferable because it is difficult to be decomposed by microorganisms.

本発明の微生物処理用成形体は、強度が高く、かつ、運転開始から目標とする処理水質に到達するまでの立上げ時間が短縮され、被処理水中の有機物の除去に優れており、特にTOC濃度が20mgC/Lというような低有機物濃度の水の処理、例えば半導体工場の排水処理や半導体産業等で用いられる超純水の使用後の回収システム等に組込んで使用するのに好適であるが、有機物濃度がこれより高い観賞魚や養殖魚用水の浄化、水耕栽培水の浄化、食品工場排水、厨房排水、下水など有機物を含む一般排水の処理にも適用することもできる。   The molded article for microbial treatment of the present invention is high in strength, shortened the start-up time from the start of operation until reaching the target treated water quality, and excellent in removal of organic substances in the treated water. It is suitable for use in the treatment of water with a low organic concentration such as a concentration of 20 mg C / L, such as wastewater treatment in a semiconductor factory or a recovery system after use of ultrapure water used in the semiconductor industry, etc. However, it can also be applied to purification of ornamental fish and aquaculture fish water having higher organic matter concentration, purification of hydroponics, food plant wastewater, kitchen wastewater, sewage and other general wastewater containing organic matter.

次に, 本発明を実施例により具体的に説明する。
(実施例1)
活性炭繊維M(比表面積700m2/g:ユニチカ社製 アドール A−7)と、芯成分がポリプロピレン、鞘成分がポリエチレンからなるポリオレフィン系バインダー繊維N(大和紡社製 ESC 鞘部融点:80℃)とをパラレルカードを用いて質量比(M:N)が20/80となる不織ウェブを形成した後、クロスラッパーにより不織ウェブをクロスラップさせ、ニードルパンチ装置により機械的に繊維の三次元交絡を生じさせて一体化した不織ウェブを作成した。引き続き、この不織ウェブを、130℃の温度の乾燥機中を通過させ、目付60g/m2 、厚み1.8mmのフェルト状活性炭繊維シートを作製した後、このシートをシングルフエザーで成型して、山高さ20mm、ピッチ15mmの波板状部材を得た。
Next, the present invention will be specifically described with reference to examples.
(Example 1)
Activated carbon fiber M (specific surface area 700 m 2 / g: Adol A-7 manufactured by Unitika Co., Ltd.), polyolefin binder fiber N consisting of polypropylene as the core component and polyethylene as the sheath component (ESC sheath melting point: 80 ° C. manufactured by Daiwabo Co., Ltd.) Is formed using a parallel card and a nonwoven web having a mass ratio (M: N) of 20/80 is formed. An interwoven nonwoven web was created that was entangled. Subsequently, the nonwoven web was passed through a dryer at a temperature of 130 ° C. to produce a felt-like activated carbon fiber sheet having a basis weight of 60 g / m 2 and a thickness of 1.8 mm, and then this sheet was molded with a single feather. Thus, a corrugated plate member having a peak height of 20 mm and a pitch of 15 mm was obtained.

次いで、平板状部材としてメッシュ状の織物であるポリプロピレンメッシュ(呉羽合繊社製、ポリプロピレン製網 50mm間の糸本数が35本)を用い、上記で得た波板状部材の山の稜線部分にEVA系ホットメルト接着剤を塗布して接着剤側を平板状部材上に重ね、熱処理して波板状部材がポリプロピレンメッシュに熱接着した微生物処理用成形体を得た。   Next, a polypropylene mesh (manufactured by Kureha Gosei Co., Ltd., polypropylene mesh, 35 yarns between 50 mm) is used as the flat plate member, and EVA is applied to the ridge line portion of the corrugated plate member obtained above. A hot-melt adhesive was applied, the adhesive side was stacked on a flat plate member, and heat treated to obtain a molded article for microbial treatment in which the corrugated plate member was thermally bonded to the polypropylene mesh.

この微生物処理用成型体を上下方向に数段重ね合わせ、EVA系ホットメルト接着剤で接着してブロック状微生物処理用成形体Aを得た。(サイズ:400×400×400mm)
(実施例2)
平板状部材として、ポリプロピレンメッシュの代わりに合成樹脂フイルム(東レ社製、無延伸ポリプロピレンフイルム 厚み100μm)を使用した以外は、実施例1と同様にして微生物処理用成形体Bを得た。
(比較例1)
平板状部材として、ポリプロピレンメッシュの代わりにポリプロピレン不織布(目付40g/m2)を使用した以外は、実施例1と同様にして微生物処理用成形体Cを得た。
This molded article for microbial treatment was overlapped several times in the vertical direction and adhered with an EVA hot melt adhesive to obtain a molded article A for block microbial treatment. (Size: 400 × 400 × 400mm)
(Example 2)
A molded product B for microbial treatment was obtained in the same manner as in Example 1 except that a synthetic resin film (manufactured by Toray Industries Inc., unstretched polypropylene film thickness 100 μm) was used as the flat plate member instead of the polypropylene mesh.
(Comparative Example 1)
A molded article C for microbial treatment was obtained in the same manner as in Example 1 except that a polypropylene nonwoven fabric (weight per unit area: 40 g / m 2 ) was used as the flat plate member instead of the polypropylene mesh.

次いで、図2に示す生物処理装置を用い、別々の処理槽4にそれぞれ微生物処理用成形体A(実施例1)、微生物処理用成形体B(実施例2)、微生物処理用成形体C(比較例1)を充填し(固定床)、全有機炭素量(TOC)の除去を行なった。この場合、エアポンプ7で処理槽4内に空気を10ml/秒の割合で吹込んだ。また、被処理水は、メタノール、アセトン及びイソプロパノールを主成分として含むTOC濃度約20mgC/Lの水で、これを処理槽4での滞留時間が10分となるように供給した。   Next, using the biological treatment apparatus shown in FIG. 2, the microorganism treatment molded body A (Example 1), the microorganism treatment molded body B (Example 2), and the microorganism treatment molded body C ( Comparative Example 1) was filled (fixed bed) and the total organic carbon content (TOC) was removed. In this case, air was blown into the treatment tank 4 by the air pump 7 at a rate of 10 ml / second. The water to be treated was water having a TOC concentration of about 20 mg C / L containing methanol, acetone and isopropanol as main components, and was supplied so that the residence time in the treatment tank 4 was 10 minutes.

運転時間(経過時間)と、得られた処理水のTOC測定結果との関係を図3に示す。なお、TOC測定は、TOC計(島津製作所(株)製 TOC−5000)を用いて行った。   FIG. 3 shows the relationship between the operation time (elapsed time) and the TOC measurement result of the obtained treated water. In addition, TOC measurement was performed using the TOC meter (Shimadzu Corporation TOC-5000).

図3から明らかなように、実施例1、2の微生物処理成形体A、Bを用いると、処理開始後約10日後には所定の処理性能が発揮されるのに対して、比較例1の微生物処理成形体Cを用いると、排水と活性炭繊維との接触効率が悪いためか効果の発揮する時間が約20日目からであった。   As is clear from FIG. 3, when the microorganism-treated molded bodies A and B of Examples 1 and 2 are used, a predetermined treatment performance is exhibited about 10 days after the start of the treatment. When the microorganism-processed molded article C was used, the time when the effect was exhibited was from about the 20th day because the contact efficiency between the waste water and the activated carbon fiber was poor.

また、微生物処理成形体Cを使用した装置では、約20日後〜60日後まではTOC濃度が約4mgC/lで安定していたが、平板状部材に使用している不織布の強度不足のためか約60日目を過ぎるころから形が崩れだし、120日をすぎると形態保持ができなくなり、TOC濃度も上昇したので測定を中止した。   In addition, in the apparatus using the microorganism-treated molded body C, the TOC concentration was stable at about 4 mg C / l from about 20 days to 60 days later, but is this because of insufficient strength of the nonwoven fabric used for the flat plate member? The shape started to collapse after about 60 days, and after 120 days, the shape could not be retained and the TOC concentration increased, so the measurement was stopped.

一方、微生物処理成形体A、Bは、180日をすぎても形が崩れるなどの問題は生じることがなく、また、処理水質も、約2〜3mgC/lで安定していた。   On the other hand, the microorganism-treated molded bodies A and B did not have a problem such as the shape being lost after 180 days, and the treated water quality was stable at about 2 to 3 mg C / l.

本発明の微生物処理用成形体の基本構造を示す説明図である。It is explanatory drawing which shows the basic structure of the molded object for microorganisms treatment of this invention. 本発明の生物処理装置の一実施態様を示す説明図である。It is explanatory drawing which shows one embodiment of the biological treatment apparatus of this invention. 運転時間(経過時間)と、得られた処理水のTOC測定結果との関係を示すグラフである。 X 微生物処理用成形体 1 波板状部材 2 平板状部材 3 透孔 4 処理槽 5 被処理水タンク 6 ポンプ 7 エアポンプIt is a graph which shows the relationship between operation time (elapsed time) and the TOC measurement result of the obtained treated water. X Molded body for microbial treatment 1 Corrugated plate member 2 Flat plate member 3 Through hole 4 Treatment tank 5 Water tank to be treated 6 Pump 7 Air pump

Claims (3)

平板状部材と、活性炭繊維を含有する波板状部材とが重ねられてなる成形体であって、前記平板状部材が織編物で構成され、かつ、波板状部材の山高さが5〜100mm、山のピッチが5〜100mmであることを特徴とする微生物処理用成形体。   A molded body in which a flat plate member and a corrugated plate member containing activated carbon fibers are overlaid, wherein the flat plate member is composed of a woven or knitted fabric, and the peak height of the corrugated plate member is 5 to 100 mm. A molded article for microbial treatment, wherein the pitch of the mountain is 5 to 100 mm. 平板状部材と、活性炭繊維を含有する波板状部材とが重ねられてなる成形体であって、前記平板状部材が合成樹脂フイルムで構成され、かつ、波板状部材の山高さが5〜100mm、山のピッチが5〜100mmであることを特徴とする微生物処理用成形体。   A molded body in which a flat plate member and a corrugated plate member containing activated carbon fibers are overlaid, wherein the flat plate member is made of a synthetic resin film, and the peak height of the corrugated plate member is 5 to 5. A molded article for microbial treatment, which is 100 mm and has a mountain pitch of 5 to 100 mm. 請求項1又は2記載の微生物処理用成形体を微生物担体として用いた生物処理装置。
A biological treatment apparatus using the microorganism treatment molded article according to claim 1 or 2 as a microorganism carrier.
JP2003352298A 2003-10-10 2003-10-10 Microbiologically treatable molding and biological treatment apparatus Pending JP2005111441A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102491498A (en) * 2011-12-16 2012-06-13 北京化工大学 Ecological carbon-fiber composite, preparation method thereof and sewage treatment reactor containing ecological carbon-fiber composite

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102491498A (en) * 2011-12-16 2012-06-13 北京化工大学 Ecological carbon-fiber composite, preparation method thereof and sewage treatment reactor containing ecological carbon-fiber composite

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